Oxidation of As（Ⅲ） by potassium permanganate

The oxidation of As（Ⅲ） with potassium permanganate was studied under conditions including pH, initial As（Ⅲ） concentration and dosage of Mn（Ⅶ）. The results have shown that potassium permanganate was an effective agent for oxidation of As（Ⅲ） in a wide pH range. The pH value of tested water was not a significant factor affecting the oxidation of As（Ⅲ） by Mn（Ⅲ）. Although theoretical redox analyses suggest that Mn（Ⅶ） should have better performance in oxidization of As（Ⅲ） within lower pH ranges, the experimental results show that the oxidation efficiencies of As（Ⅲ） under basic and acidic conditions were similar, which may be due to the adsorption of As（Ⅲ） on the Mn（OH）2 and MnO2 resulting from the oxidation of As（Ⅲ）.     

Photodegradation of bisphenol A in Fe(Ⅲ)-oxalate complexes solution

Introduction B isphenol A (2, 2-bis (4-dihydroxydiphenyl) propane) (BPA ) is w idely used as a raw m aterial for polycarbonate and epoxy resins. In previous studies, the residue level of B PA w as detected to be at a rather high level in natural w ater en…     

Exposure-response of Cr(III)-organic complexes to Saccharomyces cerevisiae

Hexavalent chromium [Cr(VI)] bioreduction produces soluble Cr(III)-organic complexes. The Cr(III)-organic complexes are relatively stable once they are formed, and no data about their toxicity were reported. Therefore, this study aims to investigate the bioavailability and toxicity of the soluble Cr(III)-organic complexes. Saccharomyces cerevisiae L-1 wild type yeast strain was chosen as the model organism and Cr(III)-citrate was selected as the representative compound of the Cr(III)-organic complexes. The short-term chronic aquatic toxicity tests of the Cr(III)-citrate was explored by measuring growth inhibition, direct viable cell count, dry biomass, biosorption, and the amount of CO₂ production. Cr(III)-citrate exerted a toxicity of 51 mg/L with an EC ₅₀, which was calculated from the percent growth inhibition. These toxicity data would be helpful to define the toxic potential of the organo-chromium-III compounds in the environment.     

含铬固体废渣中Cr~(3+) 的氧化

研究了ｐＨ、温度对铬渣中Ｃｒ３＋的氧化速率的影响．结果表明，在碱性条件下，空气中的氧气具有相当强的氧化性，足以将Ｃｒ３＋氧化为Ｃｒ６＋，且随ｐＨ、温度的升高而加快．     

ESR study of Fe(III) and Cr(III) hydroxides

The authors would like to thank Dr. A. Relier and B. Spring (University of Zürich) for providing the DSC analysis. This research was supported by the Swiss National Foundation, project no. 2.942-0.88 and by a grant of the Board of the Swiss Federal Institute of Technology.     

Photolysis of Fe (III)-hydroxy complexes as sources of OH radicals in clouds,fog and rain

Photolysis of the monohydroxy complex of Fe(III), Fe(OH)²⁺, has been proposed as a major source of OH radicals in rain. It is also a significant source of OH radicals in clouds and fog, and probably in some acidic surface waters. Fe(OH)²⁺ is the dominant monomeric Fe(III)-hydroxy complex between pH 2.5 and 5, based on currently available equilibrium constants for Fe(III)-hydroxy complexes. Quantum efficiencies for the photolysis of Fe(OH)²⁺ are 0.04±0.04 at 313 nm and 0.017±0.003 at 360 nm (293 K, ionic strength = 0.03 M). The measured rate constant for midday June sunlight photolysis of Fe(OH)²⁺ is 6.3 × 10⁻⁴s⁻¹ (half life = 18 min). Model calculations based on measured quantum yields and absorption spectra are in satisfactory agreement with measured sunlight photolysis rates of monomeric Fe(III).     

Simultaneous oxidation of Mn(II) and As(III) on cupric oxide (CuO) promotes As(III) removal at circumneutral pH

Oxidation of Mn(II) or As(III) by molecular oxygen is slow at pH < 9, while they can be catalytically oxidized in the presence of oxide minerals and then removed from contaminated water. However, the reaction mechanisms on simultaneous oxidation of Mn(II) and As(III) on oxide mineral surface and their accompanied removal efficiency remain unclear. This study compared Mn(II) oxidation on four common metal oxides (γ-Al₂O₃, CuO, α-Fe₂O₃ and ZnO) and investigated the simultaneous oxidation and removal of Mn(II) and As(III) through batch experiments and spectroscopic analyses. Among the tested oxides, CuO and α-Fe₂O₃ possess greater catalytic activity toward Mn(II) oxidation. Oxidation and removal kinetics of Mn(II) and As(III) on CuO indicate that O₂ is the terminal electron acceptor for Mn(II) and As(III) oxidation on CuO, and Mn(II) acts as an electron shuttle to promote As(III) oxidation and removal. The main oxidized product of Mn(II) on CuO is high-valent MnO_x species. This newly formed Mn(III) or Mn(IV) phases promote As(III) oxidation on CuO at circumneutral pH 8 and is reduced to Mn(II), which may be then released into solution. This study provides new insights into metal oxide-catalyzed oxidation of pollutants Mn(II) and As(III) and suggests that CuO should be considered as an efficient material to remediate Mn(II) and As(III) contamination.     

Shewanella oneidensis MR-1异化还原Fe(III)介导的As(III)氧化转化

在实验室模拟条件下,研究了Shewanella oneidensis MR-1作用下Fe(III)还原和As(III)氧化动力学及其影响因素.结果表明,Fe(III)被还原为Fe(II)的同时伴随着As(III)氧化为As(V);S. oneidensis MR-1 在含低浓度As(III)培养基上生长良好,在高浓度培养基上生长被抑制;As(III)通过制约菌体的生长与活性来抑制Fe(III)异化还原.同样,适量浓度的Fe(III)含量对As(III)氧化转化有很强的促进作用,但是过高浓度的Fe(III)浓度使得溶液中产生过多的Fe(II),从而对As(III)氧化转化有一定程度的抑制作用.此外,弱碱环境更有利于As(III)氧化转化.